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Impacts of Bottom Trawling
on Fisheries, Tourism, and the Marine Environment
Margot L. Stiles, Julie Stockbridge, Michelle Lande, Michael F. Hirshfield
May 2010
Belize bottom trawl. J.Stockbridge
Impacts of Bottom Trawling
Bottom trawl nets are used to catch
shrimp and fish living on the
seafloor from shallow coastal waters
to extreme depths of 6,000 feet (2km)
(Morgan & Chuenpagdee 2003). In
addition to the shrimp, many other
animals are captured and later
discarded, including undersized fish
(Kelleher 2005, Clucas 1997). Shrimp
trawling is one of the most
indiscriminate kinds of fishing
because the small mesh used to
retain the shrimp allows few other
animals to escape (Kelleher 2005).
When the weighted nets and trawl
doors are dragged along the
seafloor, everything in their path is
disturbed or destroyed, including
seagrasses, coral reefs or rock
gardens where fish hide from
predators (Roberts et al. 2005).
Untrawled corals
Bottom trawling uses heavily
weighted nets that are dragged
across the ocean floor. Metal
“doors” that can weigh more than
several hundred pounds are used to
hold open the net, which can be as
large as 40 feet tall and 200 feet wide
(Morgan & Chuenpagdee 2003, Stiles
et al. 2007). In some regions,
additional weights and hard rubber
wheels are added to the front of the
net.
Trawled rubble
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Fish dumped by trawlers in Belize attract pelicans. P.Lobel
Fish Thrown Away
Bottom trawling is one of the most
destructive ways to catch fish, and is
responsible for up to half of all
discarded fish and marine life
worldwide (Kelleher 2005). Valuable
fish, turtles, seabirds, marine
mammals and other animals are all
captured and discarded by bottom
trawls, and many do not survive
(Morgan & Chuenpagdee 2003). In a
side-by-side comparison, bottom
trawling for spot prawns threw away
nine times as much bycatch as more
selective fishing gear (Reilly et al.
2002).
In the Gulf of Mexico, scientists
estimate that for every pound of
shrimp caught, between four and ten
pounds of marine resources are
thrown away (Harrington et al. 2005,
Nance and Scott-Denton 1997,
Alverson et al. 1994). Shrimp
trawling in the Caribbean and
Central America also has high
discard rates, with shrimp trawls in
Panama discarding more than 80%
of their catch (Teutscher 1999 in
Kelleher 2005). Even small-scale
fisheries catch high percentages of
unwanted fish and marine resources
when using bottom trawls, including
Brazil as well as Trinidad and
Tobago (Kelleher 2005). In 2007,
shrimp trawlers in Belize landed
only 19 metric tons of shrimp (FAO)
and likely discarded about 76 to 190
metric tons of other marine life. The
fish thrown away by bottom trawlers
in Belize are probably a third of total
spiny lobster landings for the same
year.
Unwanted fish caught in bottom trawl. R. Visser, Greenpeace
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Fly fishing in the cayes. M. Paz, Green Reef, Marine Photobank
Impact on Fisheries
Shrimp trawls compete directly with
traditional cast nets, a less wasteful
and more fuel-efficient gear which
catches higher quality shrimp
(Ramos et al. 1997).
Fish that are “unwanted” and
discarded by the bottom trawler are
often juveniles of valuable species
caught by other fishermen.
Caribbean bottom trawls commonly
catch juvenile grouper and snapper
(Clucas 1997) and Gulf of Mexico
shrimp trawls catch significant
numbers of red snapper, porgy, and
mackerel (Harrington et al. 2005). In
Belize, scientists working near
bottom trawlers see slicks of
snappers and other dead fish in their
wake (P. Lobel, symposium
presentation).
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Bottom trawling often leads to
overfishing because the gear is not
selective and discards a lot of dead
fish. Overfishing by bottom trawls is
a direct threat to local fishing
communities and to tourism from
sport fishing.
Young snapper discarded by trawler in Belize. P. Lobel
Lobster fisherman. J. Stockbridge
Impact on Fisheries (continued)
Local fishermen catch fewer fish for
the same effort when competing with
bottom trawls (Whitmarsh 2003,
Ssentongo 1988). In Indonesia, local
fishermen’s catches declined 40%
after bottom trawling expanded
(JALA). Bottom trawls also conflict
with the operation of other kinds of
fishing gear, leading to disputes with
lobster and crab fishermen in the US.
Industrial trawlers operated by
foreign fleets drag through the gear
of local fishermen in Guinea,
destroying wooden canoes, other
gear, and causing personal injuries
(Lowrey 2004, EJF 2007, JALA).
Dead fish discarded by a bottom trawler. NOAA
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Spanish trawler fishing illegally at night. Oceana, J.Cuetos
Illegal fishing and the Deep Sea
Inherently destructive fishing gear is
especially dangerous when used for
illegal fishing, because a small
number of illegal fishermen can
cause a lot more damage than they
would if using more selective gear.
For this reason, banning destructive
gear is an important step against
illegal fishing, especially when
resources for enforcement are
limited. Destructive gears are also
particularly risky in offshore waters,
where law enforcement is more
difficult and deep sea fish are more
easily overexploited.
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Belize’s deep sea resources remain
unknown and are likely to include
similarly vulnerable species
(W.Heyman, pers.comm.). Many deep
sea fish are exceptionally slowgrowing, late-maturing, and do not
tolerate heavy fishing pressure
(Roberts et al. 2005 ). One of the
quickest-ever boom-and-bust
fisheries targeted a deep sea fish, the
orange roughy, which doesn’t mature
until 20 or 30 years old and lives for
more than 125 years ((Froese & Pauly
2004, Koslow et al. 2000 ).
Spotted eagle ray.Oceana, H.Kaddachi
Impact on Tourism
Ocean-based tourism involving
snorkeling, diving, and sport fishing
is one of Belize’s most important
economic activities, and is directly
threatened by discards of the marine
wildlife people most want to see.
Bottom trawling not only affects
valuable fish species, but also
threatens sea turtles, sharks and rays,
seagrasses and coral reefs (Morgan
& Chuenpagdee 2003). Tourists are
willing to pay more for a dive trip
during which they are likely to see
marine wildlife; including
approximately $30 more to see a sea
turtle, $35 to see a shark or $55 to see a
healthy coral reef (Oceana 2008).
Several endangered and threatened
species in the US are in decline
primarily because they are caught
incidentally in destructive fishing gear,
including the smalltooth sawfish.
Diver with horse-eye jacks. Oceana, H. Kaddachi
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Sea turtle caught by destructive fishing gear. NOAA
Impact on Tourism (continued)
Corals, seagrasses and other
seafloor habitats are especially
vulnerable to disturbance by bottom
trawling, and can be extremely slow
to recover (NRC 2002). Bottom
trawling flattens any upright structure
on the seafloor (NRC 2002, Koslow et
al. 2000), destroying coral reefs and
other places where juvenile fish hide.
Hard-bottom areas away from the reef
Untrawled Coral
are also likely to be vulnerable to
bottom trawling, though the impacts
may not be as long-lasting as with
deep sea corals. Recent mapping of
southern Belize waters where bottom
trawling takes place revealed a series
of small rock outcroppings, which
may provide refuges for groupers as
they move from the mangroves to the
reef (P.Lobel, pers.comm.).
Trawled Coral
Florida’s Oculina Banks. G.Gilmore, Dynamac / L.Horn, NURC, UNCW
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Bans on Bottom Trawling
Bottom trawling has been banned in many different locations worldwide:
Indonesia
The government of Indonesia banned bottom trawling to increase catches and
income for local fishermen and to end conflicts with industrial trawlers. (JALA)
Florida, Georgia, North Carolina, and South Carolina (US)
The South Atlantic Fishery Management Council banned bottom trawling in
23,000 square miles of rare deep-sea corals from North Carolina to Florida. This
ban followed the destruction of more than 90% of a nearby bank of Oculina
corals by trawling.
California, Oregon, Washington, Alaska (US)
The Pacific and North Pacific Fishery Management Councils banned bottom
trawling in more than 840,000 square miles of seafloor in the Pacific, Bering Sea,
and the Arctic. The state of California banned bottom trawling for spot prawns
to reduce discards and increase prawn catches for fishermen using more
selective gear.
Hawaii and Pacific Islands (US)
The Western Pacific Fishery Management council banned bottom trawling in 1.5
million square miles around Hawaii and other Pacific islands in US waters.
Bottom trawling is also banned in more than 330,000 square miles of the Pacific
islands from Samoa to the Mariana Trench which are protected as a National
Monument.
Azores, Madeira, and Canary Islands
Bottom trawling is banned in more than 500,000 square miles of Atlantic waters
surrounding the Canary Islands, Madeira, and the Azores.
New Zealand
The New Zealand government banned bottom trawling in large areas of
seamounts and hydrothermal vents.
Mediterranean (Europe and North Africa)
The General Fisheries Commission for the Mediterranean banned bottom
trawling in approximately 630,000 square miles of deep sea waters.
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Children play in a fishing canoe. M. Paz, Green Reef, Marine Photobank
Bottom Trawling in Belize
From Punta Gorda to Placencia,
from Sarteneja to San Pedro,
responsible fishing is critical to
maintaining healthy fisheries, reefs,
and villages.
Fishing is one of the most important
employers and sources of protein
for coastal communities in Belize.
Yet bottom trawls and other kinds of
unselective fishing gear cause harm
to other fisheries and to the marine
environment by catching juvenile
fish, damaging the seafloor, and
leading to overfishing.
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Bottom trawl nets can also harm
coral reefs, sharks, and sea turtles
that attract valuable tourism to
Belize. The majority of international
tourists come to Belize in order to
participate in an ocean-related
activity such as snorkeling, diving,
or sport fishing charters, bringing
hundreds of millions of Belize
dollars each year to the economy
(Richardson 2007).
Destructive fishing gears ruin future
development opportunities for
Belize by undermining both fisheries
and tourism, which depend on a
healthy marine environment.
References
Alverson, D.L., Freebergy, M.H., Murawski, S.A. & Pope, J.G. (1994) A global assessment of fisheries bycatch
and discards. Food and Agriculture Organization of the United Nations, Rome Committee on Ecosystem
Effects of Fishing: Phase 1 (2002) Effects of trawling and dredging on seafloor habitat. National
Research Council, National Academy Press, Washington, D.C.
Clucas, I. (1997) A study of the options for utilization of bycatch and discards from marine capture fisheries.
FAO Fisheries Circular. No. 928. Rome, FAO.
EJF (2007) Pirate Fish on Your Plate – Tracking illegally-caught fish from West Africa into the European
market. Environmental Justice Foundation, London, UK.
Froese, R. & Pauly, D., eds. (2004) “FishBase.” www.fishbase.org, version (09/2004)
Harrington, J. M., R. A. Myers and A. A. Rosenberg (2005) Wasted fishery resources: discarded by-catch in
the USA. Fish and Fisheries 6: 350-361.
JALA Advocacy Network for North Sumatra Fisherfolk in cooperation with the Environmental Justice
Foundation. When fishing turns deadly: The environmental and social impacts of illegal trawling in North
Sumatra
Kelleher, K. (2005) Discards in the world’s fisheries an update. Food and Agriculture Organization of the
United Nations, Rome
Koslow, J. A., Boehlert, G.W., Gordon, J.D.M., Haedrich, R.L., Lorance, P. & Parin, N. (2000) Continental
slope and deep-sea fisheries: implications for a fragile ecosystem. ICES Journal of Marine Science 57:548
557
Lindholm, J., Auster, P. & Valentine P. (2004) Role of a large marine protected area for conserving landscape
attributes of sand habitats on Georges Bank (NW Atlantic). Marine Ecology Progress Series 269: 61-68
Lowrey, P. (2004) SFLP: Arming fishermen with GPS to combat poachers. ICT Update, Issue 16
Morgan, L. & Chuenpagdee, R. (2003) Shifting Gears addressing the collateral impacts of fishing methods in
U.S. waters. Island Press, Washington, D.C
Nance, J., Scott-Denton, E., Martinez, E., Watson, J., Shah, A. & Foster, D. (1997) Bycatch in the southeast
shrimp trawl fishery, a data summary report, SFA Task N-10.03 National Marine Fisheries Service, Galveston
Laboratory, Galveston TX, pg. 207
National Research Council (2002) Committee on Ecosystem Effects of Fishing: Phase 1 Effects of trawling and
dredging on seafloor habitat. National Academy Press, Washington, D.C.
Reilly, P. N. and Geibel, J. (2002) Results of California Department of Fish and Game spot prawn trawl and trap
fisheries bycatch observer program 2000-2001. ,Monterey, CA. California Department of Fish and Game
Ramos, A., G. Richards, and T. Phillips (1997) Establishment of data acquisition and monitoring systems for
the Belize shrimp fishery; A description of the Belize shrimp fishery. CARICOM Fishery Research Document
No.20.
Richardson, R.B. (2007) Tourism in Belize: Vulnerability and Capacity Assessment. Submitted for Belize’s
second national communication to the United Nations Framework Convention on Climate Change
Roberts, S., Aguilar, R., Warrenchuk, J., Hudson, C. & Hirshfield, M. (2005) Deep sea life: On the edge of the
abyss. Oceana
Ssentongo, G.W. (1988) Marine fishery resources of Liberia: A review of exploited fish stocks. Food and
Agriculture Organization of the United Nations, Rome
Stiles, M., Ylitalo-Ward, H., Faure, P. & Hirshfield, M. (2007) There’s no place like home: Deep seafloor
ecosystems of New England and the Mid-Atlantic. Oceana
Teutscher, F. (1999) Shrimp bycatch, discards and utilization. First CARICOM–Cuba
Fisheries Technical Workshop, Havana. In Kelleher, K. (2005) Discards in the world’s fisheries an update.
Food and Agriculture Organization of the United Nations, Rome
Whitmarsh, D., Popitone, C., Badalmenti, F. & D’Anna, G. (2003) The economic sustainability of artisanal
fisheries: the case of the trawl ban in the Gulf of Castellammare, NW Sicily. Marine Policy, 27: 489-497
www.oceana.org
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